TETRAHYDROFURAN
HAZARDTEXT ®
Information to help in the initial response for evaluating chemical incidents
-IDENTIFICATION
SYNONYMS
TETRAHYDROFURAN FURAN, TETRAHYDRO- BUTANE, 1,4-EPOXY- BUTYLENE OXIDE CYCLOTETRAMETHYLENE OXIDE DIETHYLENE OXIDE FURANIDINE HYDROFURAN OXACYCLOPENTANE OXOLANE TETRAHYDROFURAAN (Dutch) TETRAHYDROFURAN TETRAHYDROFURANNE (French) TETRAIDROFURANO (Italian) TETRAMETHYLENE OXIDE THF BUTYLENE OXIDE, STABILIZED OXOLONE TETRAHYDROFURANO (ITALIAN)
IDENTIFIERS
USES/FORMS/SOURCES
Tetrahydrofuran is used as a solvent for high polymers, such as polyvinyl chloride and in histological techniques. It is a solvent for resins, adhesives and manufacture of lacquers. It may be used in packaging or storage containers for food in concentrations of less than 1.5% (HSDB , 2000).
-CLINICAL EFFECTS
GENERAL CLINICAL EFFECTS
- INGESTION - Tetrahydrofuran may cause nausea, dizziness, headache, and CNS depression.
- INHALATION - Vapors may be a respiratory tract irritant, or produce nausea, dizziness, and CNS depression with general anesthesia.
- OCULAR - Tetrahydrofuran is an eye irritant.
- DERMAL - Tetrahydrofuran will cause burning and dermatitis on prolonged skin exposure.
- POTENTIAL HEALTH HAZARDS - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 127 (ERG, 2004)
Inhalation or contact with material may irritate or burn skin and eyes. Fire may produce irritating, corrosive and/or toxic gases. Vapors may cause dizziness or suffocation. Runoff from fire control may cause pollution.
ACUTE CLINICAL EFFECTS
- THF is a CNS depressant and mild upper respiratory tract irritant. High concentrations produce skin irritation in experimental animals; dermal irritation or sensitation have not been reported in exposed humans (US DHHS, 1981). It has caused severe headaches (HSDB). Nausea, dizziness, and headaches in humans are readily reversed following cessation of inhalational exposure (US DHHS, 1981). Exposure to an airborne concentration of 25,000 ppm has produced loss of consciousness (RTECS). THF figured in one case of liver damage, in an interaction with prescription drugs (Edling, 1982). In one case, convulsions were due to an interaction between THF and enfluran anesthesia (Juntunen, 1984).
- THF was irritating to the skin of rabbits at concentrations greater than 20% (ACGIH, 1986). It was a CNS depressant in mice with inhalation exposure to 6.7 volume% for 5 minutes (HSDB). There was a small margin of safety between onset of anesthesia and death in dogs and mice (ACGIH, 1986), a cause for concern in human exposures. Symptoms of CNS irritation were seen in rats exposed to 5,000 ppm (Katahira, 1982b; Katahira, 1982). Short-term exposure for 4 hours decreased ciliary activity in the trachea of rabbits, and higher-level exposures produced permanent changes (Ikeoka, 1983).
CHRONIC CLINICAL EFFECTS
- There have been no reports of systemic injury from occupational exposure to THF (EOHS, 1982). One case of polyneuritis in a plastics worker exposed to THF and methyl ethyl ketone may have been due to either one or both chemicals (Viader, 1975). Other effects reported with occupational exposure to THF (as well as other chemicals) include gastritis (Contassot, 1978) and altered sensitivity to odors (Emmett, 1976).
- "Quinke's edema and lipothymic attacks" have been reported with occupational THF exposure (Tolot, 1968).
- THF was present in high concentrations in the thymus and spleen following inhalation of 3,000 ppm for 7 days in rats (Kawata & Ito, 1984). Some injury to the liver and kidneys was found in experimental animals exposed to more than 3,000 ppm for 20 days (ACGIH, 1986), but these effects may have been due to impurities (US DHHS, 1981).
- Exposure to 200 ppm for 3 or 4 weeks lowered the pulse pressure in dogs, but produced no other visible changes (ACGIH, 1986). Rats exposed to 100 or 200 ppm for 12 weeks had no apparent ill effects, while 1000 ppm increased liver function test values, and 5000 ppm caused marked local irritation and damage of the respiratory mucosa, and altered white blood cell counts, blood sugar levels, and elevated liver function test values (Katahira, 1982a; Katahira, 1982c). The presence of peroxide may be responsible for these effects (ACGIH, 1986).
- THF was found in the brain and kidney fat in dose-related concentrations in exposed rats (Elovaara, 1984).
-FIRST AID
FIRST AID AND PREHOSPITAL TREATMENT
DILUTION: If no respiratory compromise is present, administer milk or water as soon as possible after ingestion. Dilution may only be helpful if performed in the first seconds to minutes after ingestion. The ideal amount is unknown; no more than 8 ounces (240 mL) in adults and 4 ounces (120 mL) in children is recommended to minimize the risk of vomiting (Caravati, 2004).
-MEDICAL TREATMENT
LIFE SUPPORT
- Support respiratory and cardiovascular function.
SUMMARY
- FIRST AID - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 127 (ERG, 2004)
Move victim to fresh air. Call 911 or emergency medical service. Give artificial respiration if victim is not breathing. Administer oxygen if breathing is difficult. Remove and isolate contaminated clothing and shoes. In case of contact with substance, immediately flush skin or eyes with running water for at least 20 minutes. Wash skin with soap and water. In case of burns, immediately cool affected skin for as long as possible with cold water. Do not remove clothing if adhering to skin. Keep victim warm and quiet. Ensure that medical personnel are aware of the material(s) involved and take precautions to protect themselves.
INHALATION EXPOSURE INHALATION: Move patient to fresh air. Monitor for respiratory distress. If cough or difficulty breathing develops, evaluate for respiratory tract irritation, bronchitis, or pneumonitis. Administer oxygen and assist ventilation as required. Treat bronchospasm with an inhaled beta2-adrenergic agonist. Consider systemic corticosteroids in patients with significant bronchospasm. Treatment should include recommendations listed in the Oral/Parenteral Exposure section when appropriate.
DERMAL EXPOSURE EYE EXPOSURE DECONTAMINATION: Remove contact lenses and irrigate exposed eyes with copious amounts of room temperature 0.9% saline or water for at least 15 minutes. If irritation, pain, swelling, lacrimation, or photophobia persist after 15 minutes of irrigation, the patient should be seen in a healthcare facility.
ORAL/PARENTERAL EXPOSURE DILUTION: If no respiratory compromise is present, administer milk or water as soon as possible after ingestion. Dilution may only be helpful if performed in the first seconds to minutes after ingestion. The ideal amount is unknown; no more than 8 ounces (240 mL) in adults and 4 ounces (120 mL) in children is recommended to minimize the risk of vomiting. GASTRIC LAVAGE: Consider after ingestion of a potentially life-threatening amount of poison if it can be performed soon after ingestion (generally within 1 hour). Protect airway by placement in the head down left lateral decubitus position or by endotracheal intubation. Control any seizures first. ACTIVATED CHARCOAL: Administer charcoal as a slurry (240 mL water/30 g charcoal). Usual dose: 25 to 100 g in adults/adolescents, 25 to 50 g in children (1 to 12 years), and 1 g/kg in infants less than 1 year old. CNS DEPRESSION - Treatment of CNS depression is symptomatic. MONITORING PARAMETERS - Monitor renal and hepatic function. HYPOTENSION: Infuse 10 to 20 mL/kg isotonic fluid. If hypotension persists, administer norepinephrine (ADULT: Begin infusion at 0.1 to 0.5 mcg/kg/min, CHILD: Begin infusion at 0.1 mcg/kg/min), titrate to desired response.
-RANGE OF TOXICITY
MINIMUM LETHAL EXPOSURE
MAXIMUM TOLERATED EXPOSURE
3000 parts per million - chronic exposure results in respiratory irritation. 17,000 parts per million - is safe for 3 hours. 25,000 parts per million - results in anesthesia (TCLo in humans) (RTECS , 2000).
- Carcinogenicity Ratings for CAS109-99-9 :
ACGIH (American Conference of Governmental Industrial Hygienists, 2010): A3 ; Listed as: Tetrahydrofuran A3 :Confirmed Animal Carcinogen with Unknown Relevance to Humans: The agent is carcinogenic in experimental animals at a relatively high dose, by route(s) of administration, at site(s), of histologic type(s), or by mechanism(s) that may not be relevant to worker exposure. Available epidemiologic studies do not confirm an increased risk of cancer in exposed humans. Available evidence does not suggest that the agent is likely to cause cancer in humans except under uncommon or unlikely routes or levels of exposure.
EPA (U.S. Environmental Protection Agency, 2011): Not Listed IARC (International Agency for Research on Cancer (IARC), 2016; International Agency for Research on Cancer, 2015; IARC Working Group on the Evaluation of Carcinogenic Risks to Humans, 2010; IARC Working Group on the Evaluation of Carcinogenic Risks to Humans, 2010a; IARC Working Group on the Evaluation of Carcinogenic Risks to Humans, 2008; IARC Working Group on the Evaluation of Carcinogenic Risks to Humans, 2007; IARC Working Group on the Evaluation of Carcinogenic Risks to Humans, 2006; IARC, 2004): Not Listed NIOSH (National Institute for Occupational Safety and Health, 2007): Not Listed ; Listed as: Tetrahydrofuran MAK (DFG, 2002): Category 3B ; Listed as: Tetrahydrofuran Category 3B : Substances for which in vitro or animal studies have yielded evidence of carcinogenic effects that is not sufficient for classification of the substance in one of the other categories. Further studies are required before a final decision can be made. A MAK value can be established provided no genotoxic effects have been detected. (Footnote: In the past, when a substance was classified as Category 3 it was given a MAK value provided that it had no detectable genotoxic effects. When all such substances have been examined for whether or not they may be classified in Category 4, this sentence may be omitted.)
NTP (U.S. Department of Health and Human Services, Public Health Service, National Toxicology Project ): Not Listed
TOXICITY AND RISK ASSESSMENT VALUES
- EPA Risk Assessment Values for CAS109-99-9 (U.S. Environmental Protection Agency, 2011):
Reference: RTECS, 2000 LC50- (INHALATION)RAT: LCLo- (INHALATION)MOUSE: LD50- (ORAL)GUINEA_PIG: LD50- (INTRAPERITONEAL)MOUSE: LD50- (INTRAPERITONEAL)RAT: LD50- (ORAL)RAT: LDLo- (INTRAPERITONEAL)GUINEA_PIG: TCLo- (INHALATION)HUMAN:
-STANDARDS AND LABELS
WORKPLACE STANDARDS
- ACGIH TLV Values for CAS109-99-9 (American Conference of Governmental Industrial Hygienists, 2010):
Editor's Note: The listed values are recommendations or guidelines developed by ACGIH(R) to assist in the control of health hazards. They should only be used, interpreted and applied by individuals trained in industrial hygiene. Before applying these values, it is imperative to read the introduction to each section in the current TLVs(R) and BEI(R) Book and become familiar with the constraints and limitations to their use. Always consult the Documentation of the TLVs(R) and BEIs(R) before applying these recommendations and guidelines.
- AIHA WEEL Values for CAS109-99-9 (AIHA, 2006):
- NIOSH REL and IDLH Values for CAS109-99-9 (National Institute for Occupational Safety and Health, 2007):
- OSHA PEL Values for CAS109-99-9 (U.S. Occupational Safety, and Health Administration (OSHA), 2010):
- OSHA List of Highly Hazardous Chemicals, Toxics, and Reactives for CAS109-99-9 (U.S. Occupational Safety and Health Administration, 2010):
ENVIRONMENTAL STANDARDS
- EPA CERCLA, Hazardous Substances and Reportable Quantities for CAS109-99-9 (U.S. Environmental Protection Agency, 2010):
Listed as: Tetrahydrofuran Final Reportable Quantity, in pounds (kilograms): Additional Information: Listed as: Furan, tetrahydro- Final Reportable Quantity, in pounds (kilograms): Additional Information:
- EPA CERCLA, Hazardous Substances and Reportable Quantities, Radionuclides for CAS109-99-9 (U.S. Environmental Protection Agency, 2010):
- EPA RCRA Hazardous Waste Number for CAS109-99-9 (U.S. Environmental Protection Agency, 2010b):
Listed as: Furan, tetrahydro- P or U series number: U213 Footnote: Listed as: Tetrahydrofuran P or U series number: U213 Footnote: Editor's Note: The D, F, and K series waste numbers and Appendix VIII to Part 261 -- Hazardous Constituents were not included. Please refer to 40 CFR Part 261.
- EPA SARA Title III, Extremely Hazardous Substance List for CAS109-99-9 (U.S. Environmental Protection Agency, 2010):
- EPA SARA Title III, Community Right-to-Know for CAS109-99-9 (40 CFR 372.65, 2006; 40 CFR 372.28, 2006):
- DOT List of Marine Pollutants for CAS109-99-9 (49 CFR 172.101 - App. B, 2005):
- EPA TSCA Inventory for CAS109-99-9 (EPA, 2005):
SHIPPING REGULATIONS
- DOT -- Table of Hazardous Materials and Special Provisions for UN/NA Number 2056 (49 CFR 172.101, 2005):
- ICAO International Shipping Name for UN2056 (ICAO, 2002):
LABELS
- NFPA Hazard Ratings for CAS109-99-9 (NFPA, 2002):
-HANDLING AND STORAGE
STORAGE
Tetrahydrofuran must be stored in tightly sealed, dark glass bottles or steel drums affixed with the DOT-required label - FLAMMABLE LIQUID (HSDB , 1992). Pressure-vacuum venting (CHRIS , 1992)
- ROOM/CABINET RECOMMENDATIONS
Containers should be stored in cool, dark, well-ventilated areas, away from ignition sources and oxidizing materials (HSDB , 1992). Ambient storage temperature (NFPA, 1991) Inert Atmosphere: Padded (CHRIS , 1992)
Tetrahydrofuran is a very hazardous material due to its flammability and explosive properties. It is stabilized with a phenolic antioxidant which is effective under normal closed storage conditions in preventing the formation and accumulation of peroxide (HSDB , 1992). Inspect periodically for peroxide formation using potassium iodide-starch paper every time it is used. Stable unless 0.1% peroxides has accumulated because of prolonged storage in the presence of air (CHRIS , 1992; HSDB , 1992; ITI, 1988). Peroxides can be detonated by friction, impact or heating (NFPA, 1991). Separate from oxidizing materials (HSDB , 1992) NFPA, 1991).
-PERSONAL PROTECTION
SUMMARY
- RECOMMENDED PROTECTIVE CLOTHING - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 127 (ERG, 2004)
RESPIRATORY PROTECTION
- Refer to "Recommendations for respirator selection" in the NIOSH Pocket Guide to Chemical Hazards on TOMES Plus(R) for respirator information.
PROTECTIVE CLOTHING
- CHEMICAL PROTECTIVE CLOTHING. Search results for CAS 109-99-9.
-PHYSICAL HAZARDS
FIRE HAZARD
POTENTIAL FIRE OR EXPLOSION HAZARDS - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 127 (ERG, 2004) HIGHLY FLAMMABLE: Will be easily ignited by heat, sparks or flames. Vapors may form explosive mixtures with air. Vapors may travel to source of ignition and flash back. Most vapors are heavier than air. They will spread along ground and collect in low or confined areas (sewers, basements, tanks). Vapor explosion hazard indoors, outdoors or in sewers. Those substances designated with a "P" may polymerize explosively when heated or involved in a fire. Runoff to sewer may create fire or explosion hazard. Containers may explode when heated. Many liquids are lighter than water.
Tetrahydrofuran is highly volatile with a very low flash point (1 degree F), and a lower flammability limit of 2%. It is flammable over a wide range of vapor-air concentrations (HSDB , 1992; ITI, 1988).
- FLAMMABILITY CLASSIFICATION
- NFPA Flammability Rating for CAS109-99-9 (NFPA, 2002):
- FIRE CONTROL/EXTINGUISHING AGENTS
- FIRE PRECAUTIONS - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 127 (ERG, 2004)
- SMALL FIRE PRECAUTIONS - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 127 (ERG, 2004)
- LARGE FIRE PRECAUTIONS - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 127 (ERG, 2004)
Water spray, fog or alcohol-resistant foam. Use water spray or fog; do not use straight streams. Move containers from fire area if you can do it without risk.
- TANK OR CAR/TRAILER LOAD FIRE PRECAUTIONS - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 127 (ERG, 2004)
Fight fire from maximum distance or use unmanned hose holders or monitor nozzles. Cool containers with flooding quantities of water until well after fire is out. Withdraw immediately in case of rising sound from venting safety devices or discoloration of tank. ALWAYS stay away from tanks engulfed in fire. For massive fire, use unmanned hose holders or monitor nozzles; if this is impossible, withdraw from area and let fire burn.
- NFPA Extinguishing Methods for CAS109-99-9 (NFPA, 2002):
- Approach fire from upwind to avoid hazardous vapors and toxic decomposition products. Use water spray, dry chemical, "alcohol resistant" foam, carbon dioxide spray, or halon for small fires (CHRIS , 1992; ITI, 1988) NFPA, 1991).
- Do not extinguish fire unless flow from leak or spill can be stopped (HSDB , 1992).
Tetrahydrofuran vapors are heavier than air and will travel for some distance allowing for flashback along vapor trail (HSDB , 1992). Use water spray to cool fire-exposed containers (NFPA, 1991). NFPA Extinguishing Methods (NFPA, 1991): Water may be ineffective due to low flash point. However, it can be used in the form of a spray to absorb much of the heat and to keep exposed material from being damaged by fire (NFPA, 1991). Alcohol foam is recommended for water-soluble or polar flammable liquids, like tetrahydrofuran.
Do not extinguish fire unless flow from leak or spill can be stopped (HSDB , 1992).
EXPLOSION HAZARD
- Unstabilized tetrahydrofuran forms peroxides upon exposure to air or light, which if allowed to accumulate above 1% will become thermally explosive (HSDB , 1992).
- It reacts explosively with lithium-aluminum (HSDB , 1992).
- Closed containers may rupture violently when heated (NFPA, 1991).
DUST/VAPOR HAZARD
- Tetrahydrofuran vapors are heavier than air and will travel for some distance allowing for flashback along vapor trail (CHRIS , 1992; HSDB , 1992) NFPA, 1991).
- The vapor is toxic; it irritates eyes, skin, and respiratory tract; acts like a narcotic (ITI, 1988).
REACTIVITY HAZARD
- Tetrahydrofuran will not react with water or common materials (CHRIS , 1992).
- It reacts explosively with lithium-aluminum (HSDB , 1992).
- This compound reacts violently with bromine (HSDB , 1992).
- Peroxidized materials should not be dried with sodium hydroxide or potassium hydroxide, as explosions will occur (Bretherick, 1990).
- It will also react with metal halides, sodium tetrahydroaluminate, and sulfinyl chloride (Bretherick, 1990).
EVACUATION PROCEDURES
- Editor's Note: This material is not listed in the Table of Initial Isolation and Protective Action Distances.
- LARGE SPILL - PUBLIC SAFETY EVACUATION DISTANCES - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 127 (ERG, 2004)
- FIRE - PUBLIC SAFETY EVACUATION DISTANCES - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 127 (ERG, 2004)
If tank, rail car or tank truck is involved in a fire, ISOLATE for 800 meters (1/2 mile) in all directions; also, consider initial evacuation for 800 meters (1/2 mile) in all directions.
- PUBLIC SAFETY MEASURES - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 127 (ERG, 2004)
CALL Emergency Response Telephone Number on Shipping Paper first. If Shipping Paper not available or no answer, refer to appropriate telephone number: MEXICO: SETIQ: 01-800-00-214-00 in the Mexican Republic; For calls originating in Mexico City and the Metropolitan Area: 5559-1588; For calls originating elsewhere, call: 011-52-555-559-1588.
CENACOM: 01-800-00-413-00 in the Mexican Republic; For calls originating in Mexico City and the Metropolitan Area: 5550-1496, 5550-1552, 5550-1485, or 5550-4885; For calls originating elsewhere, call: 011-52-555-550-1496, or 011-52-555-550-1552; 011-52-555-550-1485, or 011-52-555-550-4885.
ARGENTINA: CIQUIME: 0-800-222-2933 in the Republic of Argentina; For calls originating elsewhere, call: +54-11-4613-1100.
BRAZIL: PRÓ-QUÍMICA: 0-800-118270 (Toll-free in Brazil); For calls originating elsewhere, call: +55-11-232-1144 (Collect calls are accepted).
COLUMBIA: CISPROQUIM: 01-800-091-6012 in Colombia; For calls originating in Bogotá, Colombia, call: 288-6012; For calls originating elsewhere, call: 011-57-1-288-6012.
CANADA: UNITED STATES:
For additional details see the section entitled "WHO TO CALL FOR ASSISTANCE" under the ERG Instructions. As an immediate precautionary measure, isolate spill or leak area for at least 50 meters (150 feet) in all directions. Keep unauthorized personnel away. Stay upwind. Keep out of low areas. Ventilate closed spaces before entering.
- If fire becomes uncontrollable and container is exposed to direct flame, evacuate for a radius of one mile. If material is leaking and not on fire, consider evacuation from downwind area based on amount of material spilled, location, and weather conditions (AAR, 1987).
- AIHA ERPG Values for CAS109-99-9 (AIHA, 2006):
Listed as Tetrahydrofuran ERPG-1 (units = ppm): 100 ERPG-2 (units = ppm): 500 ERPG-3 (units = ppm): 5000 Under Ballot, Review, or Consideration: No Definitions: ERPG-1: The ERPG-1 is the maximum airborne concentration below which it is believed nearly all individuals could be exposed for up to one hour without experiencing more than mild, transient adverse health effects or perceiving a clearly defined objectionable odor. ERPG-2: The ERPG-2 is the maximum airborne concentration below which it is believed nearly all individuals could be exposed for up to one hour without experiencing or developing irreversible or other serious health effects or symptoms that could impair an individual's ability to take protective action. ERPG-3: The ERPG-3 is the maximum airborne concentration below which it is believed nearly all individuals could be exposed for up to one hour without experiencing or developing life-threatening health effects.
- DOE TEEL Values for CAS109-99-9 (U.S. Department of Energy, Office of Emergency Management, 2010):
Listed as Tetrahydrofuran TEEL-0 (units = ppm): 50 TEEL-1 (units = ppm): 100 TEEL-2 (units = ppm): 500 TEEL-3 (units = ppm): 5000 Definitions: TEEL-0: The threshold concentration below which most people will experience no adverse health effects. TEEL-1: The airborne concentration (expressed as ppm [parts per million] or mg/m(3) [milligrams per cubic meter]) of a substance above which it is predicted that the general population, including susceptible individuals, could experience notable discomfort, irritation, or certain asymptomatic, nonsensory effects. However, these effects are not disabling and are transient and reversible upon cessation of exposure. TEEL-2: The airborne concentration (expressed as ppm or mg/m(3)) of a substance above which it is predicted that the general population, including susceptible individuals, could experience irreversible or other serious, long-lasting, adverse health effects or an impaired ability to escape. TEEL-3: The airborne concentration (expressed as ppm or mg/m(3)) of a substance above which it is predicted that the general population, including susceptible individuals, could experience life-threatening adverse health effects or death.
- AEGL Values for CAS109-99-9 (National Research Council, 2010; National Research Council, 2009; National Research Council, 2008; National Research Council, 2007; NRC, 2001; NRC, 2002; NRC, 2003; NRC, 2004; NRC, 2004; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2006; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2007; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2005; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2005; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2007; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2006; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2006; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2006; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2006; 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62 FR 58840, 1997; 65 FR 14186, 2000; 65 FR 39264, 2000; 65 FR 77866, 2000; 66 FR 21940, 2001; 67 FR 7164, 2002; 68 FR 42710, 2003; 69 FR 54144, 2004):
- NIOSH IDLH Values for CAS109-99-9 (National Institute for Occupational Safety and Health, 2007):
IDLH: 2000 ppm Note(s): [10%LEL]
CONTAINMENT/WASTE TREATMENT OPTIONS
SPILL OR LEAK PRECAUTIONS - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 127 (ERG, 2004) ELIMINATE all ignition sources (no smoking, flares, sparks or flames in immediate area). All equipment used when handling the product must be grounded. Do not touch or walk through spilled material. Stop leak if you can do it without risk. Prevent entry into waterways, sewers, basements or confined areas. A vapor suppressing foam may be used to reduce vapors. Absorb or cover with dry earth, sand or other non-combustible material and transfer to containers. Use clean non-sparking tools to collect absorbed material.
RECOMMENDED PROTECTIVE CLOTHING - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 127 (ERG, 2004) Approach release from upwind (AAR, 1987; NFPA, 1991). Eliminate all sparks, flames and ignition sources (AAR, 1987; NFPA, 1991). Stop or control leak if this can be done without personal risk (AAR, 1987; NFPA, 1991). Build pit, pond, or lagoon holding area to contain flow as necessary (AAR, 1987). Dike surface flow using soil, sand bags, foamed polyurethane, or foamed concrete (AAR, 1987). Use water spray to cool or disperse vapors. Dilute spills tend to produce nonflammable mixtures (AAR, 1987; NFPA, 1991). If the leak has not ignited, it may be flushed with water for cooling and diluting if conditions of ignition threaten (HSDB , 1992). Keep material out of water sources and sewers (AAR, 1987). Apply "universal" gelling agent to solidify encircled spill and increase effectiveness of booms (AAR, 1987). Absorb bulk liquid with fly ash, cement powder, or commercial absorbents (AAR, 1987). Small Quantities: Absorb onto paper or dissolve in petroleum ether or alcohol (higher molecular weight than butyl); then collect and remove for outdoor evaporation or safe incineration (HSDB , 1992; ITI, 1988). Large Quantities: Absorb bulk liquid with fly ash, cement powder, or commercial absorbents (AAR, 1987). Prior to implementing land treatment or disposal of waste residue consult environmental regulatory agencies (HSDB , 1992). If dissolved in water, in region of 10 ppm or greater, apply activated carbon at ten times the spilled amount (AAR, 1987). Use mechanical dredges or lifts to remove immobilized masses of pollutants and precipitates (AAR, 1987). Incineration: Tetrahydrofuran is a good candidate for liquid injection incineration at a temperature range of 650 to 1600 degrees C and a residence time of 0.1 to 2 seconds (HSDB , 1992). Incineration: It is also a good candidate for rotary kiln incineration at a temperature range of 820 to 1600 degrees C and a residence time of seconds for liquids (HSDB , 1992). Incineration: Fluidized bed incineration at a temperature range of 450 to 980 degrees C, and residence times of seconds for liquids is possible (HSDB , 1992). Peroxides: These can be removed by treatment with a strong ferrous sulfate solution made slightly acidic with sodium bisulfate (Sax & Lewis, 1989).
-ENVIRONMENTAL HAZARD MANAGEMENT
POLLUTION HAZARD
- Water: Tetrahydrofuran was found in river basins in US cities ranging from 1 to 318 ppb in the 1970s (HSDB , 1992).
- Water: The effect of low concentrations on aquatic life is unknown (CHRIS , 1992).
- Water: May be dangerous if enters water intakes. Notify local health and wildlife officials, as well as operators of nearby water intakes (CHRIS , 1992).
- Air: Air concentrations were detected at 0.173 mg/m(3) near a furan factory (HSDB , 1992).
- Tetrahydrofuran has been identified in coffee aroma (HSDB , 1992).
- Maternal milk samples were positive for tetrahydrofuran (HSDB , 1992).
ENVIRONMENTAL FATE AND KINETICS
OTHER Atmospheric fate: Degrades rapidly by photochemical reactions with hydroxyl radicals. Half-life ranges from hours to a few days. It will wash out in the rain. It will not directly photolyze in the atmosphere since it does not absorb radiation above 220 nm. Tetrahydrofuran is moderately reactive with hydroxyl radicals and with nitrogen oxides. Acrolein and formaldehyde have been reported as reaction products (HSDB , 1992). Aquatic fate: Fate is uncertain in water; it is expected to biodegrade; however, it is photostable, and it would not be expected to adsorb to the sediment. It might undergo chemical and biological oxidation, accompanied by a significant consumption of dissolved oxygen. Volatilization rate from a spill on water is unknown (HSDB , 1992). Terrestrial Fate: Tetrahydrofuran would volatilize from soil as well as leach rapidly into the ground. It is not expected to adsorb to soil due to its high water solubility; it would evaporate rapidly from a spill on soil. It biodegraded rapidly in a standard laboratory test (HSDB , 1992). Bioconcentration: Not an important consideration due to its low octanol/water partition coefficient (HSDB , 1992).
ENVIRONMENTAL TOXICITY
- ECOTOXICITY (HSDB , 1992)
Growth inhibition Microcystis (blue green algae): 225 mg/L Toxicity Threshold, protozoa: 858 mg/L Toxicity Threshold, algae: 225 mg/L
-PHYSICAL/CHEMICAL PROPERTIES
MOLECULAR WEIGHT
DESCRIPTION/PHYSICAL STATE
- Tetrahydrofuran is a colorless, mobile liquid with an ether-like or faint odor (Lewis, 1996; ACGIH, 1986) NIOSH, 1985).
VAPOR PRESSURE
- REID 7.7 psia (CHRIS , 1992)
- 0.06 atm (at 0 degrees C) (HSDB , 2000)
- 0.11 atm (at 10 degrees C) (HSDB , 2000)
- 0.173 atm (at 20 degrees C) (HSDB , 2000)
- 0.26 atm (at 30 degrees C) (HSDB , 2000)
- 145 mmHg (at 20 degrees C) (ACGIH, 1986)
DENSITY
- OTHER TEMPERATURE AND/OR PRESSURE
FREEZING/MELTING POINT
BOILING POINT
- 66 degrees C (151 degrees F) (CHRIS , 1992; Budavari, 1996)
FLASH POINT
- 1.0 degree F (Budavari, 1996)
AUTOIGNITION TEMPERATURE
- 321 degrees C (ITI, 1988)
- 610 degrees F (CHRIS , 1985)
EXPLOSIVE LIMITS
2% (NFPA, 1991) 1.8% (CHRIS , 1985)
11% (NFPA, 1991) 11.8% (NIOSH, 1990)
SOLUBILITY
Tetrahydrofuran is soluble in water (ACGIH, 1986). 30% in water at 25 degrees C (HSDB , 2000)
It is soluble in alcohols, ketones, esters, and hydrocarbons (ACGIH, 1986).
HENRY'S CONSTANT
- 1.08 X 10(-4) atm-m(3)/mol (Ehrenfeld et al, 1986)
OTHER/PHYSICAL
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